Transcript Slide 1
Genesis of the use of RothC to model soil organic carbon Outline • Composition of soil organic carbon – isolating biologically important fractions • Methodology for quantifying C allocation to fractions • Why attempt to understand allocation to fractions? • Modelling soil carbon with RothC • Substitution of conceptual with measureable C pools in RothC • MIR prediction of soil carbon fractions CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008 Composition of soil organic matter • Crop residues on the soil surface (SPR) • Buried crop residues (>2 mm) (BPR) • Particulate organic matter (2 mm – 0.05 mm) (POC) • Humus (<0.05 mm) (HumC) • Resistant organic matter (ROC) CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008 Extent of decomposition increases Rate of decomposition decreases C/N/P ratio decreases (become nutrient rich) Dominated by charcoal with variable properties Biologically significant soil organic fractions Particulate material (POC) CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008 Humus (HumC) Charcoal (ROC) Quantifying SOC allocation of SOC to fractions Total soil organic carbon Soil sieved to >2mm Quadrat collection Surface plant residue carbon Soil sieved to <2mm Na saturate, disperse, sieve <53 µm Density fractionation >53 µm fraction Buried plant residue carbon Density fractionation Particulate organic carbon Humus = <53µm - Recalcitrant CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008 <53 µm fraction Humus + recalcitrant HF treatment, UV-PO, & NMR Recalcitrant Charcoal C 25 (Mg C/ha) Organic carbon in 0-10 cm layer Variation in amount of C associated with soil organic fractions 20 Surface plant residue C (SPR) 15 Buried plant residue C (BPR) 10 Particulate organic carbon (POC) Humus C (HumC) 5 Recalcitrant C (ROC - charcoal) 0 Average for Hamilton (long term pasture) CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008 30 SPR BPR POC HumC ROC 25 20 15 10 Hamilton Hart Yass Pasture Cropped Pasture CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008 Urrbrae Mix Pasture/wheat Pulse/wheat Canola/wheat W2PF Perm Pasture Arboretum 22P 11P 0P Strat (HighN) Strat (MedN) NoTill (HighN) NoTill (MedN) 32P 0 8P 5 1P Organic C in 0-10 cm layer (Mg C/ha) Variation in amount of C associated with soil organic fractions Waikerie Mix Changes in total soil organic carbon with time Initiate wheat/fallow Total soil organic C Conversion to permanent pasture 25 (g C kg-1 soil) Soil organic carbon 30 20 15 10 5 0 10 y 18 y 0 10 20 15 CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008 30 50 40 33 43 60 70 Years Importance of allocating C to soil organic fractions Initiate wheat/fallow TOC Humus C POC ROC Conversion to permanent pasture 25 (g C kg-1 soil) Soil organic carbon 30 20 15 ~30% less humus C 10 5 10 y 18 y ~800% more POC 0 0 10 20 15 CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008 30 50 40 33 43 60 70 Years Vulnerability of soil carbon content to variations in management practices Initiate wheat/fallow Soil organic carbon (g C kg-1 soil) 30 Conversion to wheat/fallow Conversion to pasture 25 20 TOC Humus POC ROC 15 10 5 0 10 y 18 y 0 10 20 15 CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008 30 9y 50 40 33 43 60 52 70 Years Importance of quantifying allocation of C to soil organic fractions Soil 2 20 g SOC kg-1 soil Soil 1 20 g SOC kg-1 soil 10 g Char-C kg-1soil 2.5 g Char-C kg-1soil 25 15 10 5 Active C Inert C 20 (g C kg-1 soil) 20 Soil Organic Carbon (g C kg-1 soil) Soil Organic Carbon 25 15 10 5 0 0 Time CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008 Active C Inert C Time Summary SOC fractions Total soil organic carbon Soil sieved to >2mm Quadrat collection Surface plant residue carbon Soil sieved to <2mm Na saturate, disperse, sieve <53 µm Density fractionation >53 µm fraction Buried plant residue carbon Density fractionation Particulate organic carbon Humus = <53µm - Recalcitrant CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008 <53 µm fraction Humus + recalcitrant HF treatment, UV-PO, & NMR Recalcitrant Charcoal C RothC Model (Version 26.3) Plant Inputs DPM Decomposition RPM CO2 BIO Decomposition HUM Fire IOM CO2 BIO HUM Decomposition Original configuration – monthly time step CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008 Roth C data requirements • Monthly climate data: rainfall (mm), open pan evaporation (mm), average monthly air temperature (°C) • Soil clay content (% soil OD mass) • Soil cover (vegetated or bare) • Monthly plant residue additions (t C ha-1) • Decomposability of plant residue additions • Monthly manure additions (t C ha-1) • Soil depth (cm) • Initial amount of C contained in each pool CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008 RothC model structure – partitioning residue inputs into decomposable and resistant material • All plant material entering the soil is partitioned into DPM and RPM via DPM/RPM ratio Management DPM/RPM Grassland and most agricultural crops 1.44 Unimproved grassland and scrub (savannas) 0.67 Deciduous and tropical woodlands 0.25 CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008 RothC model structure – amount of each type of carbon decomposed • The amount of carbon associated with each pool that decomposes follows an exponential decay Y Y0 1 e-abckt a = the rate modifying factor for temperature b = the plant retainment rate modifying factor c = the rate modifying factor for soil water k = the annual decomposition rate constant for a type of carbon t = 0.0833, since k is based on a yearly decomposition rate. Values of k for each SOC fraction (y-1) BioF 0.66 BioS 0.66 CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008 DPM 10 RPM 0.15 Hum 0.02 RothC model structure – calculation of rate constant modifying factors • Temperature modifying factor (a) 1 e 106 tm 18.3 tm= average monthly temperature Temperature modifying factor (a) 47.9 a 7 6 5 4 3 2 1 0 -10 0 10 20 30 40 Monthly average temperature (°C) • Plant retainment modifying factor (b) b = 0.6 if soil is vegetated b = 1.0 if soil is bare CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008 RothC model structure – calculation of rate constant modifying factors Water present in the soil (mm) • Soil water modifying factor – calculated based on top soil moisture deficit (TSMD) Saturation Upper Limit Total porosity TSMD Lower Limit Dry CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008 RothC model structure – calculation of rate constant modifying factors • Calculation of maximum TSMD MaxTSMD covered (20.0 + 1.3 (%clay) - 0.01 in cm 23 (%clay)2) depth 5 MaxTSMD bare MaxTSMD covered 9 • Calculation of accumulated TSMD over each time step TSMDacc TSMDinitial rain 0.75PanEvap under the constraint that the accumulated TSMD can only vary between 0 and MaxTSMD CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008 RothC model structure – calculation of rate constant modifying factors • Calculation of the rate modifying factor (c) if TSMDacc < 0.444 MaxTSMD then c=1.0 otherwise, MaxTSMD TSMDacc MaxTSMD 0.444MaxTSMD c 0.2 1.0 0.2 1.0 c 0.2 0.444 MaxTSMD CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008 MaxTSMD RothC model structure – amount of each type of carbon decomposed • The amount of carbon associated with each pool that decomposes follows an exponential decay Y Y0 1 e-abckt a = the rate modifying factor for temperature b = the plant retainment rate modifying factor c = the rate modifying factor for soil water k = the annual decomposition rate constant for a type of carbon t = 0.0833, since k is based on a yearly decomposition rate. Values of k for each SOC fraction (y-1) BioF 0.66 BioS 0.66 CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008 DPM 10 RPM 0.15 Hum 0.02 RothC Model (Version 26.3) Plant Inputs DPM Decomposition RPM CO2 BIO Decomposition HUM Fire IOM CO2 BIO HUM Decomposition CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008 RothC model structure – partitioning of decomposition products • Fraction decomposing organic matter that goes to CO2, humus and biomass • Partitioning to CO2 is defined by clay content 7 CO2 to (Bio+ Hum) ratio 6 5 0.0786 × %Clay CO2 1.67 1.85 1.6 e Bio + Hum 4 3 2 1 0 CSIRO. 0 50 100 Clay content by mass) Soil carbon modelling workshop(% Adelaide 25-26/06/2008 Biomass + Humus partitioning 46% Bio 54% Hum Amount of soil organic carbon (Mg C/ha for 0-30 cm layer) RothC output under constant inputs and climate – to define equilibrium SOC 120 100 TOC DPM 80 RPM HUM 60 IOM BIOF 40 BIOS 20 0 0 100 200 300 400 Years since start of simulation CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008 500 Modelling the measurable Plant Inputs DPM Decomposition RPM CO2 BIO Decomposition HUM Fire IOM CO2 BIO HUM Decomposition RPM = POC IOM = ROC (Charcoal C) HUM = TOC – (POC + ROC) CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008 Requirements for calibration Soil samples Representative composite soil samples collected at the beginning and end of a period >10 years to a soil depth of 30 cm. Bulk density Measured at time of sampling using soil core weight/volume. Crop yields Yield of grain and pasture over each year to be modelled and estimates of harvest index and root/shoot ratios Management Details of individual crops, rotations, fallow periods, stubble burning and incorporation. If grazing occurred, estimates of consumption and return from animals. Climate Details of average monthly air temperature, rainfall and pan evaporation CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008 Model calibration and verification sites Calibration Sites Verification Sites Brigalow Tarlee 0 350 700 Kilometres CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008 Brigalow calibration site: influence of modifying RPM decomposition constant (k) RPM k=0.15 70 70 DPM 60 60 RPM Soil C (Mg C/ha) Soil C (Mg C/ha) RPM k=0.30 50 40 30 20 IOM 40 BIO 30 Soil POC 20 HUM 10 10 0 1982 HUM 50 1987 1992 1997 Year CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008 0 1982 CHAR TOC 1987 1992 Year 1997 Model Verification: (sites with archived soil samples) Wagga – wheat/pasture Tamworth – wheat/fallow 50 40 20 0 1988 1990 1992 1994 1996 1998 Soil C (t/ha) Soil C (t/ha) 60 40 30 Measured POC 20 10 HUM CHAR 0 1970 1980 Year 1990 2000 Year TOC Modeled Salmon Gums – wheat/wheat 50 40 30 20 10 0 1979 Soil C (t/ha) Soil C (t/ha) Salmon Gums - wheat/ 3 pasture 1983 1987 1991 Year CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008 50 40 30 20 10 0 1979 DPM RPM HUM IOM BIO 1983 1987 Year 1991 Soil Model verification: (paired sites) Kindon - pasture 15 y Dunkerry South - crop 30 Soil C (t/ha) Soil C (t/ha) 50 40 30 20 10 0 1986 20 10 0 1991 1996 2001 1967 1977 Year 1987 1997 Year Measured Modeled POC CHAR DPM HUM BIO HUM TOC RPM IOM Soil • Is this result due poor model performance or poor pairing of the sites? • Did the sites start off similar or were there significant initial differences in soil/plant/environmental properties? CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008 Quantifying SOC allocation of SOC to fractions Total soil organic carbon Soil sieved to >2mm Quadrat collection Surface plant residue carbon Soil sieved to <2mm Na saturate, disperse, sieve <53 µm Density fractionation >53 µm fraction Buried plant residue carbon Density fractionation Particulate organic carbon Humus = <53µm - Recalcitrant CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008 <53 µm fraction Humus + recalcitrant HF treatment, UV-PO, & NMR Recalcitrant Charcoal C Predicting total organic carbon and its allocation to SOC fractions using MIR Intensity Fourier Transform Infrared Spectrum 4 3 2 1 5000 4500 4000 3500 3000 2500 2000 1500 1000 500 Frequency (cm-1) CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008 • Dependence on soil chemical properties • Prediction of allocation of carbon to fractions via calibration and PLS Prediction of total organic carbon (TOC) MIR predicted TOC (g C/kg soil) 177 Australian soils (all states) from varying depths within the 0-50 cm layer n = 177 Range: 0.8 – 62.0 g C/kg R2 = 0.94 Measured TOC (g C/kg soil) CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008 Janik et al. 2007 Aust J Soil Res 45 73-81 Tasmanian soils project MIR predicted LECO C (g/kg) 250 Sample specific calibration 200 y = 0.99x + 0.58 2 R = 0.99 150 100 Generic calibration 50 y = 0.35x + 15.95 2 R = 0.86 0 0 50 CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008 100 150 200 LECO measured C (g/kg) 250 MIR prediction of particulate organic carbon MIR predicted POC (g C/kg soil) 141 Australian soils (all states) from varying depths within the 0-50 cm layer n = 141 Range: 0.2 – 16.8 g C/kg R2 = 0.71 Variability in crop residue type exits Measured POC (g C/kg soil) CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008 Janik et al. 2007 Aust J Soil Res 45 73-81 MIR prediction of charcoal C MIR predicted Char C (g/kg) 121 Australian soils (all states) from varying depths within the 0-50 cm layer n = 121 Range: 0.0 – 11.3 g C/kg R2 = 0.86 Measured Char C (g/kg) CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008 Janik et al. 2007 Aust J Soil Res 45 73-81 Summary • Methodologies exist to quantify biologically significant pools of carbon • Understanding the dynamics of the pools allows accurate interpretation of potential changes • Substitution of measureable fractions for conceptual pools in models is possible • Rapid methods for predicting soil carbon allocation to pools exist CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008 CSIRO Land and Water Jeff Baldock Research Scientist Phone: +61 8 8303 8537 Email: [email protected] Web: http://www.clw.csiro.au/staff/BaldockJ/ Acknowledgements Jan Skjemstad, Kris Broos, Evelyn Krull, Ryan Farquharson, Steve Szarvas, Leonie Spouncer, Athina Massis Thank you Contact Us Phone: 1300 363 400 or +61 3 9545 2176 Email: [email protected] Web: www.csiro.au Model Calibration Brigalow South ws64 (RPM 0.15) 0-30 cm Soil C (t/ha) 70 Measured POC HUM 60 CHAR 50 TOC 40 Modeled DPM 30 RPM 20 HUM IOM 10 BIO 0 1982 Soil 1987 CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008 Year 1992 1997 Defining soil C dynamics at Roseworthy, SA under continuous wheat production Average growing season (Apr-Oct) rainfall (mm) 338 Water limited potential grain yield (Mg/ha) 4.56 Grain yield used (Mg/ha) (85% water use efficiency) 3.88 Harvest index (Mg grain/Mg dry matter) 0.45 Total shoot dry matter production (Mg/ha) 8.62 Equilibrium conditions (model for 500 years) Soil clay content (%) Amount of C in 0-30cm layer (Mg C/ha) C content of 0-10 cm layer (%) 5 65 2.32 15 78 2.79 30 93 3.32 CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008 Changes in soil C for different levels of average grain yield Soil organic C (0-10 cm layer) (% of total soil mass) 8.0 7.0 0.5 T/ha 6.0 1 T/ha 5.0 2 T/ha 3 T/ha 4.0 4 T/ha 6 T/ha 3.0 8 T/ha 2.0 10 T/ha 1.0 0.0 0 100 200 300 Years since start of simulation CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008 400 500 Changes in soil C for different levels of average grain yield Soil organic C (0-10 cm layer) (% of total soil mass) Shift 8.0 yield from 4 to 8 T grain/ha = 1.0 %C increase over 20 years Shift yield from 4 to 6 T grain/ha = 0.4 %C increase over 20 years 7.0 0.5 T/ha 6.0 1 T/ha 5.0 2 T/ha 3 T/ha 4.0 4 T/ha 6 T/ha 3.0 8 T/ha 2.0 10 T/ha 1.0 0.0 0 5 10 15 Years since start of simulation CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008 20 Composition of methodologically defined SOC fractions Particulate organic carbon (POC) • Fragments of plant residues >53 µm (living and dead) • Molecules sorbed to mineral particles >53 µm • Large pieces of charcoal Humus (HUM-C) • Fragments <53 µm • Molecules sorbed to particles <53 µm Recalcitrant (ROC) • Materials <53 µm that survive photo-oxidation • Dominated by material with a charcoal-like chemical structure • NMR to quantify char-C CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008 Spatial variation in soil charcoal and carbon contents (0-10 cm layer) TOC 180 160 Northern Boundary (m) 140 120 100 80 60 40 20 00 0 35 35 35 34 34 34 33 33 33 32 32 32 31 31 31 30 30 30 29 29 29 27 27 27 26 26 26 25 25 25 24 24 24 23 23 23 22 22 22 21 21 21 20 20 20 19 19 19 18 18 18 17 17 17 16 16 16 15 15 15 14 14 14 13 13 13 12 12 12 11 11 11 10 10 10 9 9 9 8 8 8 7 7 7 6 6 6 5 5 5 4 4 4 3 3 3 2 2 2 1 1 1 25 50 75 Western Boundary (m) CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008 35 100 35 34 33 32 31 30 29 28 27 26 25 24 23 22 21 20 19 18 17 16 15 14 13 12 11 10 9 8 7 6 5 4 3 2 1 200 180 160 140 2.40 0.50 0.45 2.00 0.40 1.60 1.20 0.35 0.30 Northern Boundary (m) 200 Inert OC 120 100 80 60 0.25 40 0.80 0.20 0.40 0.00 0.15 0.10 20 00 0 35 35 35 34 34 34 33 33 33 32 32 32 31 31 31 30 30 30 29 29 29 27 27 27 26 26 26 25 25 25 24 24 24 23 23 23 22 22 22 21 21 21 20 20 20 19 19 19 18 18 18 17 17 17 16 16 16 15 15 15 14 14 14 13 13 13 12 12 12 11 11 11 10 10 10 9 9 9 8 8 8 7 7 7 6 6 6 5 5 5 4 4 4 3 3 3 2 2 2 1 1 1 25 50 75 Western Boundary (m) 35 100 WF WF PPFW PPFW PPFW PPFW Perm. Past. Contour bank W O O(g) F W O O(g) F W O O(g) F W O O(g) F B Pe W B Pe W B Pe W WPP WPP WPP WW WWPPPPP WWPPPPP WWPPPPP WWPPPPP WWPPPPP WWPPPPP WOF WOF WOF W O(g) F W O(g) F W O(g) F W Pe W Pe Perm. Past Perm. Past Predicting soil organic carbon contents • Clearing of Brigalow bushland Measured fractions 70 TOC 60 POC C (t/ha) HUM 50 CHAR 40 Modelled fractions 30 TOC 20 RPM 10 HUM 0 IOM 1982 1987 1992 Year CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008 1997 Options for increasing soil carbon content • Principal: increase inputs of carbon to the soil • Maximise capture of CO2 by photosynthesis and addition of carbon to soil • Options • • • • • • • Maximise water use efficiency (kg total dry matter/mm water) Maximise stubble retention Introduction of perennial vegetation Alternative crops - lower harvest index Alternative pasture species – increased below ground allocation Addition of offsite organic materials – diversion of waste streams Green manure crops – legume based for N supply CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008 Options for increasing soil carbon content • Constraints • Soil type – protection and storage of carbon • Local environmental conditions – Dryland conditions – amount and distribution of rainfall – Irrigation – maximise water use efficiency • Economic considerations – alterations to existing systems must remain profitable • Social • Options need to be tailored to local conditions and farm business situation CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008 Defining inputs of organic carbon to soil – dryland conditions • Availability of water – amount and distribution of rainfall imposes constraints on productivity and options Mudgee, NSW 45 150 45 150 45 150 30 100 30 100 30 100 15 50 15 50 15 50 0 0 0 0 0 0 Month of(mm) the year Rain CSIRO. Soil carbon modelling workshop Adelaide(mm) 25-26/06/2008 Pan Evaporation Month of(mm) the year Rain Pan Evaporation (mm) Nov 200 Sep 60 Jul 200 May 60 Mar 200 Jan 60 Nov 250 Sep 75 Jul 250 May 75 Mar 250 Jan 75 Nov 300 Sep 90 Jul 300 May 90 Mar 300 Month of(mm) the year Rain Pan Evaporation (mm) Average monthly pan evaporation (mm) Roseworthy, SA 90 Jan Average monthly rainfall (mm) Beverly, WA Soil carbon sequestration situation Evaluating potential C sequestration in soil Potential sequestration Attainable sequestration Actual sequestration Defining factors Limiting factors Reducing factors Optimise input and reduce losses Rainfall Temperature Light Soil management Plant species/crop selection Residue management Soil and nutrient losses Inefficient water and nutrient use Disrupted biology/disease Add external sources of carbon SOCactual SOCattainable SOCpotential Stable soil organic carbon (e.g. t1/2 10 years) CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008 Reactive surfaces Depth Bulk density $$ for C sequestration – fact or fiction • There is no doubt that soils could hold more carbon • Challenge – increase soil C while maintaining economic viability • Options • Perennial vegetation • Regions with summer rainfall • Portions of paddocks that give negative returns • Reduce stocking, rotational grazing, green manure • Optimise farm management to achieve 100% of water limited potential yield • External sources of carbon • Under current C trading prices • Difficult to justify managing for soil C on the basis of C trading alone • Do it for all the other benefits enhanced soil carbon gives CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008 Incorporation into a decision support framework MIR Analysis SOC fractions Clay Climate data Soil water limits Soil C model with N and P dynamics C sequestration in soils in response to management CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008 Soil fertility and fertiliser addition rate calculators Crop growth Options for sequestering carbon Photosynthesis CO2 Mineralisation Plant production Death/Harvest Burning Recalcitrant organic C (ROC) Plant residues Increasing extent of decomposition Particulate organic C Humus organic C Carbon sequestration options 1) increase C stored in plants – e.g. grow a forest 2) move more carbon into the recalcitrant pool increase CAdelaide stored in one or all soil components CSIRO. 3) Soil carbon modelling workshop 25-26/06/2008 Soil animals and microbes What determines soil organic carbon content? Soil organic carbon = content f Inputs of Losses of , organic carbon organic carbon Inputs • Net primary productivity • Addition of waste organic materials CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008 Losses • Conversion of organic C to CO2 by decomposition Balance between inputs and outputs 25 (g C kg-1 soil) Soil organic carbon 30 Inputs >> Outputs 20 Inputs > Outputs 15 Inputs = Outputs Inputs < Outputs 10 Inputs << Outputs 5 0 0 20 40 60 80 100 120 140 Years CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008 Amount of carbon in the 0-10 cm layer (Mg C/ ha) Understanding the residue input requirements to change soil carbon content Amount of C required: 24 Mg C 50 Mg Dry Matter (DM) 90 80 70 60 50 48 40 1% SOC Rate per year (no losses): 2% SOC 10 Mg DM/y SOC 50% allocation below 3% ground SOC equates to 5 Mg shoot4%DM/y 30 24 20 10 0 0.9 1 1.1 1.2 1.3 5% SOC Rate per year (with 50% loss) 20 Mg DM/y (50% loss) 50% allocation below ground 10 Mg1.5shoot1.6DM/y1.7 1.4 Bulk density (g/cm3) CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008 Nutrients associated with soil carbon Assumptions: C/N =10 and C/P=120) 140 BD = 1.0 1600 BD = 1.2 1400 BD = 1.4 1200 BD = 1.6 1000 800 600 400 Amount of P (kg/ha) Amount of N (kg/ha) 1800 120 BD = 1.0 BD = 1.2 BD = 1.4 100 BD = 1.6 80 60 40 20 200 0 0 0.0 0.2 0.4 0.6 0.8 1.0 0.0 0.2 0.4 0.6 0.8 1.0 Change in soil carbon (% of soil mass) Change in soil carbon (% of soil mass) CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008 CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008 Variation in C/N ratio of different fractions of soil organic matter 120 Upper boundry C/N ratio (weight basis) 100 Lower boundry 80 60 40 20 0 SPR CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008 Humus POM BPR Type of organic matter Minimum requirements for tracking soil organic carbon for accounting purposes 1. Collection of a representative soil sample to a minimum depth of 30 cm 2. An accurate estimate of the bulk density of the sample 3. An accurate measure of the organic carbon content of a soil sample For 0-30 cm soil with a bulk density of 1.0 Mg/m3 and a carbon content of 1.0% Bulk Mass of Carbon Depth x density x content = 30 Mg C/ha Carbon = (cm) (g/cm3) (Mg C/ha) (%) CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008 Dynamic nature of SOC and its fractions 32 (Mg C ha-1in 0-10 cm) Amount of organic C Irrigated Kikuyu pasture – Waite rotation trial TOC POC Humus ROC 24 16 8 0 1/6/98 6/2/99 14/10/99 20/6/00 Date of sample collection CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008 25/2/01 Dynamic nature of SOC and its fractions (Mg C ha-1 in 0-10 cm) Amount of organic C Dryland Pasture/Wheat/Wheat – Waite rotation trial 36 32 28 24 20 16 12 8 4 0 1/6/98 TOC 6/2/99 POC Humus 14/10/99 20/6/00 Date of sample collection CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008 ROC 25/2/01 Correcting soil carbon for management induced changes in bulk density Management induced compaction Original soil surface Original 30 cm depth New 30 cm depth Soil bulk density (Mg/m3) 1.1 1.2 1.3 1.4 Mass Soil 0-30 cm (Mg/ha) 3300 3600 3900 4200 Depth for equivalent mass (cm) 30.0 27.5 25.4 23.6 1% OC, no BD correction 33 36 39 42 1% OC, with BD correction 33 33 33 33 Organic C loading (Mg/ha) CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008 Predicted equilibrium soil organic C contents for 3 regions in SA with different climate type Clare Roseworthy Waikerie Growing season rain (mm) 491 338 170 Water limited potential grain yield (T/ha) 6.2 4.6 1.8 Grain yield (T/ha) (85% WUE) 5.3 3.9 1.5 Total shoot dry matter (T/ha) 11.7 8.6 3.4 Modelled amount of C in 0-30 cm (t C/ha) 98 78 41 Estimated %C in 0-10 cm soil layer 3.5 2.8 1.5 Equilibrium soil carbon content CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008 Take home messages • Organic matter (carbon + other elements) is composed of a variety of materials and improves soil productivity • Different soils can hold different amounts of carbon • Nature of soil minerals, depth and bulk density • Balance between inputs and losses – goal is to maximise production per mm available water • Measuring changes in soil carbon requires careful consideration • Options to increase carbon must be tailored to the local conditions and economic considerations of the farmer • Computer models exist to predict the impact of management on soil carbon CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008 Tasmanian soils project • Samples • 154 soils collected from 0-10 cm layer of a diverse set of soil x management combinations • 30 measured values used to derive the calibration • All other samples predicted from this calibration • Range of Walkley-black C contents • 3.7 – 99.9 g C/kg soil CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008 100 MIR predicted carbon content (g/kg) • Objective: Prediction of total organic carbon 80 60 40 20 y = 0.60x + 25.90 R2 = 0.37 0 0 50 100 150 -20 Measured carbon content (g/kg) Tasmanian soils project 250 120 Measured Walkley-Black C (g/kg) MIR predicted LECO (g/kg) y = 0.99x + 0.58 R2 = 0.99 200 150 100 50 y = 0.43x + 12.83 R2 = 0.61 100 80 60 40 20 0 0 0 100 200 300 Measured LECO C (g/kg) CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008 0 100 200 300 Measured LECO C (g/kg) Functions of organic matter in soil Biological functions - energy for biological processes - reservoir of nutrients - contributes to resilience Functions of SOM Physical functions Chemical functions - improves structural stability - cation exchange capacity - influences water retention - buffers changes in pH - alters soil thermal properties - complexes cations CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008 Distribution and turnover of organic carbon in soil 0 cm SOC content Proportion of profile SOC Relative response time High 30-50% Rapid Low 20-30% Intermediate to slow Very low 10-30% Slow 10 cm 30 cm 100 cm CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008 Variation in soil organic carbon with depth for different soils Soil organic carbon content (% by weight) 0 1 0 1 0 1 2 0 1 2 3 0 2 4 Soil Depth (cm) 0 50 100 150 200 Red brown earths CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008 Grey clays Red earths Black earths Krasnozems 6 Significance of carbon in soils World wide C pools (1015 g C) • Atmosphere (CO2C) 780 • Living Biomass (plants, animals) 550 • Soil 0-1 m depth 1500 0-3 m depth 2300 1330 Houghton (2005) Annual fluxes (1015 g C/yr) Emissions Responses • Fossil fuel burning 6 • Land use change 2 CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008 • Atmospheric increase 3 • Oceanic uptake 2 • Other 3 Potential for soils to sequester C Potential does exist to sequester C in soil 0 cm 10 cm • SOC pool size: 1500 Pg • Rapid cycling SOC: 500-750 Pg • 1% increase in stored SOC/yr: 5 - 7.5 Pg/yr 30 cm • CO2-C emissions: 8 Pg/yr Issues • Permanency of increase • Native unmanaged soils • Constraints on C inputs (biophysical, economic, social) 100 cm CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008 Take home messages • Soil organic matter provides many benefits to soil • Different soils can hold different amounts of carbon • Soil carbon represents the balance between additions and losses • Soil carbon is composed of a variety of materials • Understanding soil carbon composition allows more accurate assessment of management impacts • Measuring changes in soil carbon requires careful consideration • Computer models exist to predict the impact of management on soil carbon • Options to improve soil carbon and productivity need to be tailored to local conditions CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008 Understanding the residue input requirements to change soil carbon content Amount of carbon in the 0-10 cm layer (Mg C/ ha) Amount of C required: 14 Mg C 28 Mg90Dry Matter (DM) 80 Rate per 70year (no losses): 5.6 Mg 60 DM/y 50% allocation below ground 50 2.8 Mg shoot DM/y 1% SOC 2% SOC 3% SOC 40 28 30year (with 50% loss) Rate per 20 DM/y (50% loss) 11.2 Mg 50% allocation below ground 10 5.6 Mg0 shoot DM/y 0.9 1 1.1 1.2 5% SOC 14 1.3 1.4 Bulk density (g/cm3) CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008 4% SOC 1.5 1.6 1.7 Soil organic carbon content: influence of management • Defining the influence of management practices on soil organic carbon is difficult • Different types of organic C respond at different rates • POC - years to decades • Humus – decades to centuries • Charcoal – centuries to millennia • Other factors may be more influential in some years than management (e.g. rainfall) • Spatial variability and within year temporal variability • Use of computer simulation models offers a way to estimate likely outcomes quickly • example soil carbon model: RothC CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008 Changes in soil C for different climates at a constant wheat grain yield Average grain yield of 4 T/ha Soil organic C (0-10 cm layer) (% of total soil mass) 4.0 3.0 2.0 Clare Roseworthy Waikerie 1.0 0.0 0 100 200 300 Years since start of simulation CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008 400 500 Nutrients associated with soil carbon Assumptions: C/N =10 and C/P=120) 140 BD = 1.0 1600 BD = 1.2 1400 BD = 1.4 1200 BD = 1.6 1000 800 600 400 Amount of P (kg/ha) Amount of N (kg/ha) 1800 120 BD = 1.0 BD = 1.2 BD = 1.4 100 BD = 1.6 80 60 40 20 200 0 0 0.0 0.2 0.4 0.6 0.8 1.0 0.0 0.2 0.4 0.6 0.8 1.0 Change in soil carbon (% of soil mass) Change in soil carbon (% of soil mass) CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008 Significance of carbon in soils •World wide C pools (1015 g C) • Atmosphere (CO2C) • Living Biomass (plants, animals) • Soil 0-1 m depth 0-3 m depth 780 550 1330 1500 2300 Houghton (2005) •Annual fluxes (1015 g C/yr) •Emissions •Responses • Fossil fuel burning 6 • Land use change 2 CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008 • Atmospheric increase 3 • Oceanic uptake 2 • Other 3 Cation exchange capacity (meq/100g C) Chemical function: Cation exchange capacity 600 500 400 300 200 POM Humus 100 Recalitrant 0 4 5 6 7 Soil pH CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008 8 9 Questions remaining – from an organic matter perspective • What is the capacity of soils to store organic matter (carbon and nutrients)? • How much of the carbon and nutrients stored in soil organic matter can be made available to microbes and plants? • What are the potential effects of alternative and new management options on organic matter levels? • Further quantification of the role of soil organic fractions is required to extend the range of soil types and environments examined. • What is the role of external sources of organic matter and do their influences persist? CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008 Significance of carbon in soils •World wide C pools (1015 g C) • Soil • Atmosphere (CO2) • Living Biomass (plants, animals) Soil in Australia 1500 720 560 30 World fluxes (1015 g C/year) Fossil Vegetation Missing Atmospheric Ocean + Uptake + Sink Fuel + Destruction = Increase 5 1.8 2.2 3 1.6 0.1% increase in soil organic C = 1.5 CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008 Adding charcoal to soil : the Terra Preta phenomenon Terra Preta • High soil organic carbon – significant charcoal • High P contents – 200–400 mg P/kg • Higher cation exchange capacity • Higher pH and base saturation CSIRO. Soil carbon modelling workshop Adelaide 25-26/06/2008 Oxisol